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ARCHIVED REPORTS_XR0007878
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ARCHIVED REPORTS_XR0007878
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Last modified
10/8/2020 10:49:26 PM
Creation date
6/23/2020 3:01:04 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0007878
RECORD_ID
PR0507217
PE
2950
FACILITY_ID
FA0007741
FACILITY_NAME
AUTO ZONE INC
STREET_NUMBER
1100
Direction
N
STREET_NAME
WILSON
STREET_TYPE
WAY
City
STOCKTON
Zip
95202
APN
11733035
CURRENT_STATUS
02
SITE_LOCATION
1100 N WILSON WAY
P_LOCATION
01
QC Status
Approved
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EHD - Public
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N7XXMA <br /> Working To Restore Nature <br />' Addendum One to Remedial Action Plan March 1, 1993 <br /> Coca-Cola Former Distribution Facility, Stockton, California 54006.01 <br /> four other borings. Soil type was primarily clayey and sandy silt. Cumulative results of <br /> laboratory analyses of sort samples are summarized in Tables A-1 and A-2, and are listed <br /> 1 under October/November 1990 data TPHg was nondetectable in all eleven borings, with <br /> the exception of B-15/VEW-2 and B-16/VEW-3. TPHg in these two borings ranged from <br /> nondetectable to 630 ppm (at 5 feet in B-16/VEW-3). TPHd was nondetectable in all <br /> borings except B-14/VEW-1 through B-17/VEW-4, and ranged from nondetectable to 50 <br /> ppm (in B-16/VEW-3 at 15 feet). BTEX was nondetectable in five of the borings, and in <br /> the other six borings ranged from nondetectable to 44 ppm total xylenes (in B-16/VEW-3) <br />' TPHg soil concentration contours at depths of 0 to 30 feet are shown graphically in Plate <br /> 4. PNAs were nondetectable in all of the 14 samples tested, with the exception of B- <br /> 16/VEW-3 which contained 3,500 ppm naphthalene at a depth of 5 feet, as reported in <br /> Table A-2 <br />' In November 1990, the groundwater sample from newly constructed well MW-6 indicated <br /> nondetectable concentrations of TPHg, and BTEX. TPHd was detected at a concentration <br /> of 64 ppb <br /> Preliminary_Vapor Extraction Test <br />' In November 1990, a preliminary vapor extraction test was conducted to determine the <br /> feasibility of using vapor extraction as a soil remediation alternative (USTEC, September <br /> 1991). The test was conducted on VEW-1 through VEW-4 and MW-1, MW-4, and MW-5 <br />' Applied wellhead vacuums ranged from about 50 to 66 inches of water. Induced vacuums <br /> in the observation wells were measured, and ranged from 0.1 to about 6 inches of water <br /> Distances between wells ranged from 12.5 to 94 5 feet. Extracted soil vapor concentrations <br />' were not determined, nor was the effective radius of influence. One year later in November <br /> 1991,four additional vapor extraction wells (VEW-5 through VEW-8)were installed. These <br /> four new wells were not previously tested for a soil vapor extraction system. Boring logs for <br /> 1 these four wells were included in the fourth quarter 1991 momtormg report (USTEC, 1992), <br /> but results of soil laboratory analyses for these vapor wells were not available to RESNA <br /> at this writing. <br /> uarterly Groundwater Monitoring, <br /> Quarterly groundwater monitoring was initiated after the wells were installed. Table A-4 <br /> summarizes depth to water (DTW) measurements and groundwater elevations. DTW <br /> ranges from about 67 feet to about 71 feet, and groundwater elevation is about 52 feet <br /> below mean sea level (MSL). The groundwater flow direction is generally toward the <br /> northeast, at a shallow gradient of about 0.002 feet per foot. <br />' A-4 <br />
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